Anthurium caloveboranum
Croat
Pays · région · aire protégée · écorégion · biome
Graphe en cours d’indexation
Calcul du tissu écologique de Anthurium caloveboranum.
Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).
Liste rouge IUCN
VU · Vulnérablecritères B1ab(iii)↘Décroissante- Évaluation
- 2013 · v3.1
- Altitude
- 0 – 2000 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Seventeen specimens of this species have been collected between 1974 and 1987. There are no population data.
Menaces identifiées(11 menaces classées CMP-IUCN)
4_1Roads & railroadsUnknownUnknownOngoing9_1_3Type Unknown/UnrecordedUnknownUnknownOngoing1_1Housing & urban areasOngoing2_1_1Shifting agricultureOngoing2_1_2Small-holder farmingOngoing2_1_3Agro-industry farmingOngoing2_2_3Scale Unknown/UnrecordedOngoing2_3_2Small-holder grazing, ranching or farmingOngoing2_3_3Agro-industry grazing, ranching or farmingOngoing3_2Mining & quarryingOngoing
+ 1 menaces supplémentaires
Description complète des menacesTexte détaillé évaluation IUCNExpert
Subsistence and commercial agriculture have supplanted native forest throughout the Isthmian moist forests. Flat areas have been converted to banana, coffee and pineapple plantations, while steeper areas have been logged and converted to cattle pasture. New roads have encouraged more human settlement of the region, and many of the forests are under tremendous logging pressure. Gold mining and pollution also threaten this region, even around protected areas. Although the montane forests are under less threat and more patches remain than in the lowlands, erosion is a major concern in the Talamancan highlands due to the conversion of forest to pasture. While the Talamanca Montane forest is relatively well protected, the recent but drastic elimination of middle elevation habitats in surrounding ecoregions has isolated the highland reserves and made their populations vulnerable to genetic degradation (WWF 2001).
Habitats préférentiels (classification IUCN)
1_6Forest - Subtropical/Tropical Moist Lowland1_9Forest - Subtropical/Tropical Moist Montane
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Several subpopulations of this species (half of those actually known) are found within protected areas, with a good history of management and community involvement. About 20% of its extent of occurrence is composed of protected areas, which include: Palo Seco Protected Forest, La Fortuna Forest Reserve, and the General de Division Omar Torrijos Herrera and Santa Fe National Parks. No ex situ conservation measures are in place for this species.
Actions de conservation (2)Conservation Actions Classification Scheme — IUCNExpert
3_4_1Captive breeding/artificial propagation3_4_2Genome resource bank
Stress écologiques (20)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation
Usage & commerce (2)Use & Trade — IUCNExpert
13Pets/display animals, horticultureinternationalnational16Establishing ex-situ production *
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Neotropical
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Epiphyte
Références bibliographiques (6)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2013. IUCN Red List of Threatened Species (ver. 2013.1). Available at: <a href="http://www.iucnredlist.org">http://www.iucnredlist.org</a>. (Accessed: 12 June 2013).
- WCSP. 2008. World Checklist of Selected Plant Families. Facilitated by the Royal Botanic Gardens, Kew. Available at: <a href="http://www.kew.org/wcsp/monocots/">http://www.kew.org/wcsp/monocots/</a>. (Accessed: 2008).
- Powell, G., Palminteri, S. and Schipper, J. 2001. Talamancan montane forests (NT0167). Available at: <a href="http://worldwildlife.org/ecoregions/nt0167">http://worldwildlife.org/ecoregions/nt0167</a>.
- Powell, P., Palminteri, S. and Schimper, J. 2001. Isthmian-Pacific moist forests (NT0130). Available at: <a href="http://www.nationalgeographic.com/wildworld/profiles/terrestrial/nt/nt0130.html">http://www.nationalgeographic.com/wildworld/profiles/terrestrial/nt/nt0130.html</a>.
- Powell, G., Palminteri, S. and Schipper, J. 2001. Isthmian-Atlantic moist forests (NT0129). Available at: <a href="http://worldwildlife.org/ecoregions/nt0129">http://worldwildlife.org/ecoregions/nt0129</a>.
- Croat, T.B. 1986. <i>Revision of the genus </i>Anthurium<i> of Mexico and Central America, part II: Panama</i>. Missouri Botanical Garden.
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Crook, V.
evaluator
Scott, J.A.
Crook, V. 2013. Anthurium caloveboranum. The IUCN Red List of Threatened Species 2013: e.T44392182A44453695. Accessed on 05 May 2026.
Distribution mondiale
Calcul de la distribution GBIF· ~10–60 s
Phénologie
Calcul du calendrier d'apparition· ~5–30 s